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[[file:RG pic1.jpg|thumb|300px|alt=photo of a rain garden|<font size=3>Bioinfiltration (rain garden) in a residential development. Photo courtesy of Katherine Sullivan.</font size>]] | [[file:RG pic1.jpg|thumb|300px|alt=photo of a rain garden|<font size=3>Bioinfiltration (rain garden) in a residential development. Photo courtesy of Katherine Sullivan.</font size>]] | ||
− | Infiltration is the practice of draining water into soils, typically through engineered systems such as rain gardens, infiltration basins, grass swales and detention | + | Infiltration is the practice of draining water into soils, typically through engineered systems such as <span title="Bioretention, also called rain gardens, is a terrestrial-based (up-land as opposed to wetland) water quality and water quantity control process. Bioretention employs a simplistic, site-integrated design that provides opportunity for runoff infiltration, filtration, storage, and water uptake by vegetation. Bioretention areas are suitable stormwater treatment practices for all land uses, as long as the contributing drainage area is appropriate for the size of the facility. Common bioretention opportunities include landscaping islands, cul-de-sacs, parking lot margins, commercial setbacks, open space, rooftop drainage and street-scapes (i.e., between the curb and sidewalk). Bioretention, when designed with an underdrain and liner, is also a good design option for treating Potential stormwater hotspots. Bioretention is extremely versatile because of its ability to be incorporated into landscaped areas. The versatility of the practice also allows for bioretention areas to be frequently employed as stormwater retrofits."> '''bioinfiltration'''</span> (rain gardens), <span title="Infiltration basins, infiltration trenches, dry wells, and underground infiltration systems capture and temporarily store stormwater before allowing it to infiltrate into the soil. As the stormwater penetrates the underlying soil, chemical, biological and physical processes remove pollutants and delay peak stormwater flows."> [https://stormwater.pca.state.mn.us/index.php?title=Infiltration '''infiltration basins''']</span>, <span title="Dry swales, sometimes called grass swales, are similar to bioretention cells but are configured as shallow, linear channels. They typically have vegetative cover such as turf or native perennial grasses. Dry swales may be constructed as filtration or infiltration practices, depending on soils."> [https://stormwater.pca.state.mn.us/index.php?title=Dry_swale_(Grass_swale) '''dry swales''']</span> with <span title="A check dam is a structure installed perpendicular to flow in a natural or manmade conveyance channel to reduce flow velocity. By slowing flow velocities, check dams can serve multiple functions including reduction of channel scour and erosion, enhancement of sediment trapping, and greater treatment of the water quality control volume via enhanced water detention or retention. Typical check dam materials include rock, earth, wood, and concrete. "> '''check dams'''</span>, and <span title="Permeable pavements allow stormwater runoff to filter through surface voids into an underlying stone reservoir for temporary storage and/or infiltration. The most commonly used permeable pavement surfaces are pervious concrete, porous asphalt, and permeable interlocking concrete pavers (PICP)."> '''[https://stormwater.pca.state.mn.us/index.php?title=Permeable_pavement permeable pavement]'''</span>. The practice of infiltration is beneficial for soils, maintaining natural hydrology, and has a significant water quality impact for downstream lakes, rivers, and ponds. Depending on design, infiltration practices can be a key component of GI to promote the health and well-being of animals, vegetation, and the people that rely upon these waters when designing sites. |
− | + | Some of the more common infiltration practices include | |
*infiltration basins and trenches, | *infiltration basins and trenches, | ||
*rain gardens, | *rain gardens, | ||
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*tree trenches. | *tree trenches. | ||
− | For further reading on different types of infiltration, [[Stormwater infiltration Best Management Practices]] and [[BMPs for stormwater infiltration]]. | + | For further reading on different types of infiltration, see [[Stormwater infiltration Best Management Practices]] and [[BMPs for stormwater infiltration]]. |
==Green infrastructure and multiple benefits== | ==Green infrastructure and multiple benefits== |
Infiltration is the practice of draining water into soils, typically through engineered systems such as bioinfiltration (rain gardens), infiltration basins, dry swales with check dams, and permeable pavement. The practice of infiltration is beneficial for soils, maintaining natural hydrology, and has a significant water quality impact for downstream lakes, rivers, and ponds. Depending on design, infiltration practices can be a key component of GI to promote the health and well-being of animals, vegetation, and the people that rely upon these waters when designing sites.
Some of the more common infiltration practices include
For further reading on different types of infiltration, see Stormwater infiltration Best Management Practices and BMPs for stormwater infiltration.
Green infrastructure (GI) encompasses a wide array of practices, including stormwater management. Green stormwater infrastructure (GSI) encompasses a variety of practices primarily designed for managing stormwater runoff but that provide additional benefits such as habitat or aesthetic value.
There is no universal definition of GI or GSI (link here for more information). Consequently, the terms are often interchanged, leading to confusion and misinterpretation. GSI practices are designed to function as stormwater practices first (e.g. flood control, treatment of runoff, volume control), but they can provide additional benefits. Though designed for stormwater function, GSI practices, where appropriate, should be designed to deliver multiple benefits (often termed "multiple stacked benefits". For more information on green infrastructure, ecosystem services, and sustainability, link to Multiple benefits of green infrastructure and role of green infrastructure in sustainability and ecosystem services.
Maximizing specific green infrastructure (GI) benefits of constructed areas requires design considerations prior to installation. While site limitations cannot always be overcome, the following recommendations for a designer are given to maximize the GI benefit.
Note: Under the Minnesota Construction Stormwater Permit GI, particularly infiltration, must be considered first when selecting stormwater treatment methods. However, if Class D soils are present on the site infiltration practices cannot be used. Class A soils are the most desirable for infiltration but infiltration systems can also be successful with B or C soils. --- Maybe add a chart indicating soil penetrability of different HSG groups —
The Minnesota Stormwater Manual offers a chart to help designers with a cost-benefit analysis for infiltration linked here. The Pollution Control Agency allows for infiltration to be used as a credit source when meeting pollutant budgets for Total Suspended Solids (TSS) and Total Phosphorus (TP). The methodology for counting credits can be found here. Additional Information:
Support material Outside MSM Links to include/reference: Y - good picture graphic for infiltration and groundwater recharge and simple explanation of groundwater - https://www.usgs.gov/special-topics/water-science-school/science/infiltration-and-water-cycle
Y - Reference for part of above built table - neat pictures - https://www.ashbyma.gov/plan/subdivision%20docs/breitmaier/160923%20plans-docs/Stormwater%20Report/BMP%20-%20Infiltration%20Basin.pdf
Y - Cost benefit table - https://stormwater.pca.state.mn.us/index.php/Cost-benefit_considerations_for_infiltration
M - good guidelines for developing green infrastructure though - https://coast.noaa.gov/data/docs/digitalcoast/gi-cost-benefit.pdf
Decent picture - Infiltration and the Water Cycle | U.S. Geological Survey (usgs.gov)
Additional References from the Minnesota Stormwater Manual